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` FFaZanaerobic <br /> derlying sandy silt strata in the exploratory boring. Rust mottling occurs when <br /> cteria decompose organic matter and use iron(Fe") in their metabolic processes. <br /> n of iron creates rust. When these two conditions are present - organic matter and <br /> �. environment - denitrification (the conversion of nitrate to gaseous products and thee by which nitrate concentrations are reduced) is promoted. Although mottling may <br /> be attributed to geologic processes, it is most probably due to seasonal soil saturation whereby <br /> percolating soil water encounters slower permeability strata and accumulates on top of this strata. <br /> Soil samples were obtained from two areas in proposed leachfield areas for chemical analyses. <br /> The first sample was composited from subsamples obtained from 40 inches below grade in <br /> Parcels 1 through 7. As the noted on the SOIL ANALYSIS REPORT under SAMPLE <br /> NUMBER PL1-7,the nitrate-nitrogen(NO3-N) concentration is a very low 2 ppm. For <br /> ` comparison purposes,the second sample was obtained from the vineyard in Parcel 8, and is <br /> referenced under SAMPLE NUMBER as GRPS. The nitrate-nitrogen concentration is also very <br /> low at 4 ppm. <br /> Soil chemistry was done on the samples to analyze several constituents. The important <br /> parameters for nitrate loading assessment are the organic matter, pH, cation exchange capacity <br /> (CEC), clay content percentage, soluble salts, along with nitrate-nitrogen content. As noted,the <br /> soluble salts are low at 0.3 mmhos/cm. Organic matter in the soil is also low at 0.8%, with an <br /> estimated nitrogen release (ENR) of 46 lbs NO3-N per acre. This indicates a very low potential <br /> for future nitrate-nitrogen loading. Since septic effluent is composed predominately of <br /> ammonium(NH4) ions,the pH, along with the CEC, are significant influences on ammonium <br /> molecules. The pH of the soil is neutral-to-somewhat alkaline which may slightly inhibit <br /> ammonium formation and stability, and may create a small propensity for ammonia(NH3) <br /> formation. <br /> The CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. <br /> The loamy sand soil with a CEC of 4.8 and 7.2 suggests there is very little potential for the <br /> ` retention of ammonium molecules for microbial uptake and suppression of nitrification(nitrate <br /> formation). The CEC probably decreases with lower soil profile depth. Clay soils have a <br /> higher CEC than other soil types. Cations(positively charged ions) such as NH4', K', Ca"and <br /> Mg" are removed from solution by the clay soil fraction because the clay particles possess a <br /> negative charge. In cation exchange, a positively charged ion within the clay complex is <br /> ., replaced and released by another type of ion. Ionic exchange, through its effects on nutrient <br /> availability and acidity, has a tremendous effect on biological and chemical transformations. <br /> The significance of cation exchange becomes important when the chemistry of septic effluent is <br /> analyzed. Nitrogen in septic tank effluent consists of approximately 75%N in the ammonium <br /> ion (NH4') form and 25%N in the organic form. If the ammonium ion is bound and eventually <br /> utilized,nitrification cannot occur. Nitrification is an aerobic reaction accomplished <br /> predominately by autotrophic bacteria which convert ammonium (NH4')to nitrite (NOD and <br /> subsequently to nitrate(NO3). <br /> 3 <br /> 'valley Ag Research <br />